Bridging the research gap between reservoir operations and inundation risks under the future climate, this study integrates a hydrologic reservoir management model with a 2D hydrodynamic model, comparing the conventional regulations and the optimized reservoir operations based on the particle swarm optimization (PSO) algorithm. Results reveal that optimized operations using the PSO algorithm consistently outperform conventional strategies by better-managing peak discharges and controlling downstream inundation. The study further differentiates between PSO-optimized plans: PSO1, which focuses on minimizing inundation areas, and PSO2, which prioritizes peak reduction at the flood control point. Interestingly, PSO2 proves superior for single-point peak reduction, typically the primary objective in current practices, whereas PSO1, despite lesser peak reduction, achieves a smaller inundation area, enhancing basin-scale flood resilience. This discrepancy reveals the need to consider downstream inundation risks as critical evaluation metrics in reservoir optimization, a factor often overlooked in existing studies. The research underscores the importance of updating operational frameworks to incorporate 2D inundation risks and adapt to increased flood risks under changing climate conditions. Despite optimization, future climate scenarios predict increased flood exposure, indicating that the current safety discharge rates and flow regulations at control points are outdated and require revision.

  • A hydrologic reservoir management model was integrated with a 2D hydrodynamic model.

  • Optimizations by the PSO algorithm outperformed the conventional regulations.

  • Aiming to reduce the peak flow and the inundation area would lead to different optimized plans.

  • The critical gap in the current practice that neglects the inundation risk is highlighted.

  • Current safety drainage standards might be outdated and need revisions.

Optimizing reservoir operations and schedules is critical for disaster prevention and water resources management. Downstream flood resilience can be maximized by identifying and implementing the optimized reservoir strategies (Serra-Llobet et al. 2022), which requires considering the potential hazard of inundation by floodwaters (Cea & Costabile 2022). The analysis of flood propagation could usually be carried out by the 2D hydrodynamic models, which are useful in forecasting the inundation conditions for residential areas (Bhandari et al. 2018), developing flood risk zones (Farhadi & Najafzadeh 2021; Erima et al. 2022), and assessing the floodplain adaptive measures (Kalra et al. 2020). However, hydrodynamic models are usually intrinsically complex and computationally expensive, so existing reservoir operational optimization often relies on simplified routing methods (Dang et al. 2020; Wei et al. 2022; Ding et al. 2023) or neglects downstream routing (Dahmani & Yebdri 2020; Nourani et al. 2020).

Flood disasters fall within the realm of hydroclimatic calamities, often intricately linked with climate change (Rahman et al. 2021; Munawar et al. 2022). The climate drivers affect the flood risk mostly through the altered peak discharge, while reservoir buildup and operations also have an influence on flood risk (Tang et al. 2021). So, reservoir management needs to be framed in variable future climates (Nourani et al. 2020; Sun et al. 2023), though such studies often mainly focus on inflow availability instead of downstream flood risk.

Given multiple variables to consider for determining the reservoir releases, various algorithms have been developed to optimize the reservoir discharge curve, such as the linear and dynamic programming (DP) (Little 1955), genetic algorithm (GA) (Anand et al. 2018), or neural networks (Zhang et al. 2018). The particle swarm optimization (PSO) algorithm, as an intelligent algorithm that mimics a flock of birds foraging for food, was first proposed by Kennedy & Eberhart (1995) and has become widely accepted as an optimization method in hydrologic models ever since. Kennedy (1997) studied the components and parameters of the PSO algorithm and gave the theoretical significance and reasonable range of each parameter. Clerc (1999) introduced the convergence parameters to improve the convergence speed of the algorithm. Spiliotis et al. (2016) used the PSO algorithm combined with the water supply modeling system to optimize reservoir regulations that effectively reduced the deficits of water supply demands during droughts. Al-Aqeeli & Mahmood Agha (2020) developed a PSO model for individual reservoirs to maximize the annual hydropower generation using the annual reservoir generation as an objective function. Diao et al. (2022) proposed a simulated annealing particle swarm optimization (SAPSO) algorithm to treat the cascading reservoir system with the objective of maximum peak reduction.

When compared to the GA, evolutionary planning, and other algorithms, the PSO algorithm was proved as an effective global optimization method (Parsopoulos & Vrahatis 2002). Mirza et al. (2020) combined DP with the PSO to propose a DP-PSO algorithm, which outperformed the DP-GA algorithm in terms of search space and computational efficiency. Zarei et al. (2019) combined the PSO with the Bat Algorithm to improve the convergence speed of the algorithm by over 20%. Jahandideh-Tehrani et al. (2020) summarized 22 existing algorithms that evolved from PSO algorithms and compared them with evolutionary algorithms and mathematical optimization algorithms, showing that most of the PSO algorithms outperformed GA, mainly in terms of faster convergence. Ma et al. (2021) proposed spark-based parallel dynamic programming and spark-based parallel particle swarm optimization (SPPSO) methods based on cloud computing and found that SPPSO algorithms converged fast and could jump out of the local optima. The PSO has also been applied to optimize reservoir operations for multi-objectives such as water supply, flood storage, and hydroelectric power production and was proved to achieve comparable effects as the non-dominated sorting genetic algorithm II (Afshar & Hajiabadi 2018; Hojjati et al. 2018).

Collectively, the reservoir optimization and downstream inundation prediction were often vaguely considered together but conducted separately, which led to great uncertainty to flood risk management at the watershed scale. If any downstream fluvial flooding is considered, most current practices relied on the 1D channel routing model to predict the hydrograph at the critical cross-section, which hardly predicts the spatial inundation areas and potential consequences, especially to the critical infrastructures at the riparian. Furthermore, current studies rarely associated the climate variations with the reservoir management for the watershed scale, other than their effects on increasing the reservoir storage and overflowing risk (Beiranvand & Rajaee 2023).

Therefore, this work delves into the correlation between reservoir optimization scheduling and downstream inundation while evaluating solutions to the challenges posed by future climate change on reservoir optimization. For this purpose, the reservoir operational model, essentially a hydrologic model, was integrated with the 2D hydrodynamic model accordingly. The effects of the conventional and optimized reservoir operations were compared during four typical historic flood events. The reservoir releases through different operations drove a hydrodynamic model to simulate the effect of reservoir management on the channel safety at critical cross-sections and the downstream inundation risk in different climate scenarios. By comprehensively considering the 2D flood inundation levels at downstream, this work transcends traditional 1D channel model-based scheduling strategies. Through the comparison of two different release plans optimized by the PSO algorithm, this work provides a new finding that points out the necessity of considering the downstream inundation during the optimization of reservoir operations. This finding not only provides water resource managers with a more effective strategy for flood risk control but also aids in enhancing the efficiency of reservoir management to confront the increasingly severe impacts of climate change.

Study site

Completed in 2015, the Nierji Reservoir was the largest water conservancy project in the Nenjiang River basin. It is located 189 km upstream of Qiqihar, which is the downstream flood control point that the Nierji reservoir protects. The upper river basin above the reservoir covers 22.35% (66,400 km2) of the entire Nenjiang River basin area, with an annual inflow of 104.7 × 108 m3, accounting for 45.7% of annual runoff in the Nenjiang River basin. As an earth–rockfill reservoir made of asphalt concrete, it was designed for the 1,000-yr flood control standard. The characteristic water levels and the corresponding storage capacity of the Nierji Reservoir were listed (Liang et al. 2021) (Table 1).

Table 1

Characteristic water levels and the corresponding storage of the reservoir

Characteristic water levelsLevel (m)Storage capacity (108 m3)
Flood-limited water level 213.37 52.2 
Normal water level 216 64.56 
Flood control high water level 218.15 75.88 
Characteristic water levelsLevel (m)Storage capacity (108 m3)
Flood-limited water level 213.37 52.2 
Normal water level 216 64.56 
Flood control high water level 218.15 75.88 

The study selected four significant historical events as design floods that occurred in the Nierji-Qiqihar reach: Type 1969 (Gao et al. 2008), Type 1988 (Gao et al. 2007), Type 1998.6 (Liu et al. 2020), and Type 1998.8 (Guan et al. 2021); the first three represent the floods coming from the reservoir point, while the last one incorporates the influence of the lateral inflows from the intermediate basins within the reach (Ding et al. 2023). Type 1998.8 represents a historical extreme case, which caused 14,800 m3/s peak flow and exceeded the safety capacity of the flood control infrastructures at Qiqihar. These pivotal design floods served as benchmarks for assessing the flood simulation tools and reservoir operations before implementation (Lu & Zhang 1999).

The performance of the Nierji Reservoir in terms of flood storage, peak reduction, and postponing the flood arrival has far-reaching implications for the normal functioning of the downstream cities such as Qiqihar with a population of 1,237,300. The suburban levee is 136 km long and is distributed along the city which is designed for a 50-yr event with a peak flow of 8,850 m3/s. The urban levee of Qiqihar is 47 km long, which is designed for a 100-yr event with a peak flow of 12,000 m3/s (Ding et al. 2023).

Particle swarm optimization

PSO is an algorithm proposed based on mimicking the bird flock foraging (Peng et al. 2011). Each particle in the algorithm ‘flies’, i.e. seeks, based on its own and other particles' flight experience. The PSO algorithm has the advantages of a concise principle, simple implementation, fast convergence, and fewer parameters, which is suitable for solving multi-objective and non-linear optimization problems. To optimize the daily discharge flows within the studied period, N particles with D variables were selected and their initial values were randomly assigned. During each iteration, each particle calculated its fitness value by the objective function. Various criteria could usually be considered as the objectives for flood control such as the maximum peak reduction, the shortest flood duration, or the minimum flood volume. In this work, the maximum peak reduction was determined to be the objective:
(1)
where qm is the maximum discharge flow at the downstream flood control point, t is time, q(t) is the reservoir discharge at time t, Qq(t) is the observed lateral inflows, and f represents the channel routing function. Based on the objective, the local optimal and the global optimal solutions of the reservoir discharge were stochastically determined through the following iterative process, and each particle could be updated as follows:
(2)
(3)
(4)
where is the velocity of the (k + 1)th iteration in the dth dimension of the ith particle, is the velocity of the kth iteration in the dth dimension of the ith particle, is the individual optimal solution for the kth iteration in the dth dimension of the ith particle, is the global optimal solution of the dth dimension, is the particle value of the kth iteration in the dth dimension of the ith particle, N is the number of particles set as 150, D is the dimensionality of the solution vector set as 34, c1 and c2 are learning rates both set as 0.7, r1 and r2 are two independent numbers randomly selected in the range [0,1], and is the inertia weight controlling the strength of the search capability.
A strategy of a linear decreasing inertia weight was proposed as follows:
(5)
where k is the current time step, kmax is the allowed maximum time step, ωini is the initial inertia weight set as 0.9, and ωend is the last inertia weight when evolving to the maximum number of iterations set as 0.4. This strategy of using adaptive inertia weight is exhibited through the tests of this study, and it is showed an improved searching effect on approaching convergence compared to the traditional means of using a constant inertia weight.
On account of the safety requirements of the reservoir and the flood control point, the solution also needed to meet the following constraints. First, the water level of the reservoir should fall within the acceptable range:
(6)
where Z is the current reservoir level, Zmin is the flood-limited water level, and Zmax is the flood prevention level. Second, the downstream discharge must not exceed the maximum allowable streamflow:
(7)
where Qdownstream is the downstream streamflow at Qiqihar, and Qsafety is the maximum safety discharge allowed at Qiqihar (8,850 m³/s for 50-yr flood and 12,000 m³/s for 100-yr flood). Third, the discharge released from the reservoir should meet the minimum demand for power generation, irrigation, and environmental baseflow, and the maximum discharge should not exceed the maximum allowed discharge rate:
(8)
where qmin is the minimum discharge required for power generation, irrigation, and downstream environmental baseflow, qt is the current reservoir discharge, and qtmax is the maximum allowed reservoir discharge. Lastly, the change of discharge between time steps is subject to the flow capacity of the spillway gates and operational convenience:
(9)
where qt+1 is the reservoir discharge flow at t + 1 time step and ΔQmax is the maximum allowable change of the reservoir discharge between adjacent time steps.

Muskingum routing

The synergetic simulation of reservoir operation and flood propagation was mostly modeled by the hydrologic Muskingum routing method (Ji et al. 2017), which was proposed for studying flood control in the Muskingum watershed in Ohio, U.S. (McCarthy 1939) and then improved by Cunge (1969). The Muskingum method was adopted in this study as the channel routing function for optimizing the reservoir operations as follows:
(10)
(11)
(12)
(13)
where C0, C1, and C2 are the Muskingum routing coefficients, respectively, Q1 and Q2 are the outflows of every reach at the current and next time steps, I1 and I2 are the inflows of every reach at the current and next time steps, K is the storage constant set as 4, x is the specific gravity factor set as 0.2, and Δt is the time step.
To increase the model accuracy, the segmental Muskingum algorithm was applied. The channel with length L could be further divided into n segments, and each segment would be modeled in a consecutive way downstream with the same set of parameters (Kl and xl):
(14)
(15)
(16)
where n is the number of river segments, Kl is the segmented storage constant set as 1, L is the total river length, Ll is the segmented river length, and xl is the segmented flow-specific gravity coefficient.

Operational strategies

Conventional operation

According to the preliminary design plan to minimize the flood peak at Qiqihar, a conventional operating model was established to represent the current operations that met the downstream flood control standard as follows (Liang et al. 2021):

  • (a) During a flood event with a less than 50-yr return period, the peak flow at Qiqihar should be less than 8,850 m³/s.

  • (b) During a flood event of the 50–100-yr return period, the peak flow at Qiqihar should be less than 12,000 m³/s.

  • (c) The operational water level of the reservoir should not exceed 216 m.

  • (d) The maximum water level of the reservoir shall be less than 218.15 m.

Optimized operation

The maximum peak reduction downstream at Qiqihar was chosen as the optimization objective. The reservoir discharge was optimized through the PSO algorithm, which should meet the safety requirements of the reservoir and, at the same time, provide storage for the beneficial use of flood water. The water level of the reservoir was updated based on a simple water balance considering the inflow and discharge.

Flood inundation risk

Based on the Type 1969 design flood as an example, the HEC-RAS software was used to simulate the 2D flood inundation in three scenarios (flood, conventional operation, and optimized operation) to analyze the flood control effects of conventional and optimized operations. In the flood scenario, the pre-dam discharge at Qiqihar was estimated by applying the flow time series of the corresponding return periods, e.g. 50 yr, as the boundary condition at the location of the reservoir to drive the 2D inundation simulation as if the dam was unbuilt. This serves as a baseline to evaluate the effects of reservoir operations.

Most of the relevant studies targeted the hydrograph of a downstream river cross-section during reservoir optimization, which failed to take account of the spatial information such as the flood inundation. Due to the stochastic diversity of the optimization method, two PSO-based optimized operations were compared for different flood scenarios. For the PSO1 plan, the peak flow at Qiqihar tended to be higher and the flood discharge dropped quickly during the receding stage. For the PSO2 plan, the peak flow at Qiqihar was relatively lower and the flood discharge was maintained at a high level during the receding stage. Both plans met all other necessary constraints. In this way, PSO2 was characterized by the lower flood peak as the common optimization objective that mainly focused on the hydrograph at the critical downstream cross-section, while PSO1 was characterized by less flood discharge during the receding stage which led to lower total volume and inundation. So, the influence of the different optimization strategies focusing on the peak reduction and inundation extents could be closely compared.

Climate scenarios

The global average precipitation was projected, based on the SSP1-2.6 scenario, to increase by approximately 2.9% (1.0–5.2%) in the phase of 2081–2100 compared to the phase of 1995–2014. In the SSP3-7.0 scenario, the global average precipitation was projected to increase by about 4.7% (2.3–8.2%) in the period of 2081–2100 compared to the period of 1995–2014 (Lee et al. 2021). Based on the simulation of the above two climate scenarios, distributed projection data were obtained on the percentage increase in winter and summer precipitation in Northeast China for the period 2081–2100 compared with the period 1995–2014.

To accommodate the phases of 2081–2100 and 1995–2014 in the climate scenarios, the Type 1998.6, 50-yr design flood, falling within the current phase, was used as the baseline. During the flooding season in the summer, the reservoir inflow was predicted to be enhanced by 0–10% in the SSP1-2.6 scenario and by 10–20% in the SSP3-7.0 scenario for the study region. For these two climate scenarios, the inflow was designed to increase by 10% and 20% correspondingly to provide indications to compare the conventional and optimized reservoir operations in the future climate. The flood inundation was simulated for those two climate scenarios, and the inundation risk was analyzed to serve as a reference for developing future flood control measures.

Comparison of the single-point operational strategies

To assess the effects of reservoir regulations and optimized operations on single-point flow control, four design flood types (1969, 1988, 1998.6, and 1998.8) were analyzed for 50-yr and 100-yr return periods (Figures 1 and 2). The results of the conventionally regulated operations and the optimized operations were compared side by side for each of the four types of design floods. Overall, both the regulated and optimized reservoir operations achieved lower flood peaks compared to the pre-dam discharge at Qiqihar, which is the downstream flood control point. Their peaks all fell below the red lines of the safety drainage rates allowed at Qiqihar. However, the optimized operations achieved lower flood peaks while holding more storage in the reservoir for beneficial use, indicating their better performance in achieving the multi-objectives. The curves of the reservoir discharge look relatively close between the two operations, indicating that both operations took the strategy of pre-releasing at the early stage of the flood. However, the improvement in the downstream peak flow and the reservoir discharge by the optimized operation is more significant for the 50-yr event than for the 100-yr event. This is similar to the previous finding that the optimized operations achieved higher improvement in flood resilience for the low-to-medium flood, which became limited for the large flood event (Ding et al. 2023).
Figure 1

Comparison of regulated and optimized reservoir operations for four types of 50-yr design floods.

Figure 1

Comparison of regulated and optimized reservoir operations for four types of 50-yr design floods.

Close modal
Figure 2

Comparison of regulated and optimized reservoir operations for four types of 100-yr design floods.

Figure 2

Comparison of regulated and optimized reservoir operations for four types of 100-yr design floods.

Close modal

The conventional regulation model, based on the established rules, describes a critical state of flood control, which just meets the downstream safety discharge rate at Qiqihar. The optimization model fully utilizes the reservoir storage and reduces the downstream discharge at Qiqihar (Table 2). Consistently, the optimization of the reservoir operations for the 50-yr design floods was relatively more effective than that for the 100-yr design floods, and the ratio of the peak reduction in the former turned out to be 3–5% higher than the latter.

Table 2

Peak reduction rates

Operating methodReturn periodFlood typeAfter-dam peak flow at Qiqihar (m3/s)Pre-dam peak flow at Qiqihar (m3/s)Peak reduction rate (%)
Conventional operation 50a 1,969 8,850 12,371.2 28.46 
1,988 8,850 12,123.8 27.00 
1,998.6 8,850 12,062.9 26.63 
1,998.8 8,850 12,213.2 27.54 
100a 1,969 12,000 15,100 20.53 
1,988 12,000 14,637.8 18.02 
1,998.6 12,000 14,342 16.33 
1,998.8 12,000 14,748.1 18.63 
Optimized operation 50a 1,969 8,326.81 12,371.2 32.69 
1,988 7,766.92 12,123.8 35.94 
1,998.6 7,578.36 12,062.9 37.18 
1,998.8 8,197.24 12,213.2 32.88 
100a 1,969 10,677.8 15,100 29.29 
1,988 9,937.59 14,637.8 32.11 
1,998.6 9,709.24 14,342 32.30 
1,998.8 10,424.3 14,748.1 29.32 
Operating methodReturn periodFlood typeAfter-dam peak flow at Qiqihar (m3/s)Pre-dam peak flow at Qiqihar (m3/s)Peak reduction rate (%)
Conventional operation 50a 1,969 8,850 12,371.2 28.46 
1,988 8,850 12,123.8 27.00 
1,998.6 8,850 12,062.9 26.63 
1,998.8 8,850 12,213.2 27.54 
100a 1,969 12,000 15,100 20.53 
1,988 12,000 14,637.8 18.02 
1,998.6 12,000 14,342 16.33 
1,998.8 12,000 14,748.1 18.63 
Optimized operation 50a 1,969 8,326.81 12,371.2 32.69 
1,988 7,766.92 12,123.8 35.94 
1,998.6 7,578.36 12,062.9 37.18 
1,998.8 8,197.24 12,213.2 32.88 
100a 1,969 10,677.8 15,100 29.29 
1,988 9,937.59 14,637.8 32.11 
1,998.6 9,709.24 14,342 32.30 
1,998.8 10,424.3 14,748.1 29.32 

To better demonstrate the difference between the two methods of determining the reservoir operations, Type 1969 floods with 50- and 100-yr return periods were picked as an example (Figure 3). Compared with the conventional operational method, the optimized operations reduced the peak of the reservoir discharge by 34.3% for the 50-yr flood but had little effect on the 100-yr event. It can also be seen that the optimization operations tend to release water during the recession stage to empty the storage for the next event. Furthermore, the optimized highest water level was very close to the flood control high water level, which serves as the maximum allowed water level for the reservoir, indicating the effective use of the reservoir storage; however, this was at the risk of downstream flood safety, which needed to be evaluated by the 2D inundation model.
Figure 3

Comparisons of reservoir discharges for 50-yr (a) and 100-yr (b) events, maximum flows at Qiqihar (c), and reservoir levels (d) corresponding to the regulated and optimized operations for the Type 1969 design flood.

Figure 3

Comparisons of reservoir discharges for 50-yr (a) and 100-yr (b) events, maximum flows at Qiqihar (c), and reservoir levels (d) corresponding to the regulated and optimized operations for the Type 1969 design flood.

Close modal

Inundation factor

The three flooding simulation scenarios were developed based on the Type 1969 design flood with the 50-yr recurrence as follows: (1) pre-dam design flood, when the Nierji Reservoir did not withhold any incoming floods; (2) conventional operation, when the reservoir withholds the incoming flood and the discharge is controlled by the conventional regulations; (3) optimized operation, when the reservoir withholds the incoming flood and the discharge is controlled by optimized operations. The boundary conditions were set up in HEC-RAS accordingly to represent the above three flooding scenarios, and their maximum inundation extents and average depths were significantly different (Figure 4 and Tables 3 and 4).
Table 3

Summary of inundation situations

ScenarioInundation area (km2)Average depth (m)
ChannelOverland
Design flood 1,443.26 5.89 1.15 
Conventional operation 1,190.25 5.87 1.22 
Optimized operation 1,024.01 5.58 1.12 
ScenarioInundation area (km2)Average depth (m)
ChannelOverland
Design flood 1,443.26 5.89 1.15 
Conventional operation 1,190.25 5.87 1.22 
Optimized operation 1,024.01 5.58 1.12 
Table 4

Optimization effects of two operations compared to the baseline (design flood)

CriteriaReduction (%)
ConventionalOptimized
Inundation area 17.53 29.05 
Channel depth 0.28 5.22 
Overland depth −5.66 3.29 
CriteriaReduction (%)
ConventionalOptimized
Inundation area 17.53 29.05 
Channel depth 0.28 5.22 
Overland depth −5.66 3.29 
Figure 4

Flooding inundations due to the 50-yr design flood (left), conventional reservoir regulation (middle), and optimized reservoir operation (right).

Figure 4

Flooding inundations due to the 50-yr design flood (left), conventional reservoir regulation (middle), and optimized reservoir operation (right).

Close modal
The effect of optimized operations on controlling the inundation area is superior to that of conventional regulations. The optimized operation reduced the inundation area by 419.25 km2, accounting for 29.05% of the total affected area, and reduced the total affected area by 116.24 km2 (9.77%) compared to the conventional regulation. In addition, the optimized operation also reduced the average flood depth in the channel by nearly 30 cm and reduced the average flood depth in the inundated overland by 3 cm. Given the large area affected by inundation, the optimized operation makes a considerable difference in the flood volume and the inundation consequence. The difference between the three flooding scenarios could be further illustrated by subtracting the depth distribution of the baseline from that of the two flooding scenarios (Figure 5). Compared with the conventional operation, the optimized operation significantly reduced the flood depth downstream, i.e. the reduction in the inundated depths by the optimized operation was larger than that in the conventional operation.
Figure 5

Differences in flood depths (m) of the conventional operation (left) and the optimized operation (right) compared to the baseline.

Figure 5

Differences in flood depths (m) of the conventional operation (left) and the optimized operation (right) compared to the baseline.

Close modal
The two PSO-optimized operations were developed with different focuses on the peak reduction at the cross-section and the inundation control. For the PSO1 operation, the peak flow at Qiqihar was 8,263.71 m3/s, and the flood discharge in the receding stage was lower; for the PSO2 operation, the peak flow at Qiqihar was 8,251.58 m3/s, while the flood discharge in the receding stage was higher (Figure 6). Although PSO2 had a better optimization effect judged from the peak reduction, its higher discharge in the receding stage resulted in a larger inundation area (Figure 7).
Figure 6

Reservoir operations optimized by PSO1 (left) and PSO2 (right).

Figure 6

Reservoir operations optimized by PSO1 (left) and PSO2 (right).

Close modal
Figure 7

Flood inundations of PSO1 (left) and PSO2 (right) optimizations.

Figure 7

Flood inundations of PSO1 (left) and PSO2 (right) optimizations.

Close modal

Therefore, the effect of the optimized reservoir management could be graded differently with and without considering the inundation process. If the single-point peak discharge was used as the optimization objective as a common practice, the PSO2 optimized operation, which achieved 12.13 m3/s lower peak flow than the PSO1 operation, should be regarded as a better strategy. However, the comparison of the inundation areas indicates that the PSO1 operation, achieving the lower inundated area, could be regarded as a better strategy for reducing flood exposure (Table 5). Such conflict indicates the necessity of adding the downstream inundation risk as an additional optimization objective or an evaluation metric, which, however, was neglected by most current studies.

Table 5

Summary of inundations

ScenarioPeak flow at Qiqihar (m3/s)Inundation area (km2)Average depth (m)
ChannelOverland
PSO1 8,263.71 1,055.54 5.658 1.150 
PSO2 8,251.58 1,084.49 5.648 1.132 
ScenarioPeak flow at Qiqihar (m3/s)Inundation area (km2)Average depth (m)
ChannelOverland
PSO1 8,263.71 1,055.54 5.658 1.150 
PSO2 8,251.58 1,084.49 5.648 1.132 

Climate factor

To accommodate the climate phases of 2081–2100 and 1995–2014 as the climate scenarios, the three scenarios (Type 1998.6, 50-yr flood as the baseline, 10% enhanced climate scenario, and 20% enhanced climate scenario) were developed to drive the inundation simulations through HEC-RAS (Figure 8 and Tables 6 and 7). The two enhanced climate scenarios only slightly increased the flooding depth but rather significantly expanded the inundation area by 11.60% and 20.85% for the 10% enhanced and 20% enhanced scenarios, respectively. The average flood depth in the channel only increases by 1.83% and 3.53% for the 10% enhancement and 20% enhancement scenarios, respectively. This is in consistence with the previous finding of this region that the flood risk would increase under future climate conditions (Sun et al. 2023).
Table 6

Summary of inundations under different climate scenarios

ScenarioInundation area (km2)Average depth (m)
ChannelOverland
1998.6 flood 1,583.40 6.050 1.202 
10% enhanced 1,767.03 6.161 1.253 
20% enhanced 1,913.58 6.264 1.270 
ScenarioInundation area (km2)Average depth (m)
ChannelOverland
1998.6 flood 1,583.40 6.050 1.202 
10% enhanced 1,767.03 6.161 1.253 
20% enhanced 1,913.58 6.264 1.270 
Table 7

Climate effects compared to the baseline (design flood)

CriteriaIncrease (%)
10% water enhancement20% water enhancement
Inundation area 11.60 20.85 
Chanel depth 1.83 3.53 
Overland depth 4.21 5.59 
CriteriaIncrease (%)
10% water enhancement20% water enhancement
Inundation area 11.60 20.85 
Chanel depth 1.83 3.53 
Overland depth 4.21 5.59 
Figure 8

Pre-dam inundations due to the design flood (left), 10% enhanced scenario (middle), and 20% enhanced scenario (right).

Figure 8

Pre-dam inundations due to the design flood (left), 10% enhanced scenario (middle), and 20% enhanced scenario (right).

Close modal
The reservoir operations under the two climate scenarios were further optimized by the PSO algorithm (Figure 9). However, based on the current objective and constraints, no viable solutions could be found after 3,000 iterations as the peak flow at Qiqihar would always exceed the current safety standard. In the 10% water enhancement scenario, the peak flow at Qiqihar reached 9,044.03 m3/s after optimization, while in the 20% water enhancement scenario, the peak flow at Qiqihar even reached 10,700.82 m3/s after optimization, both of which were above the safety drainage rate of 8,850 m3/s.
Figure 9

Optimized reservoir operations in the 10% enhanced scenario (a) and 20% enhanced scenario (b).

Figure 9

Optimized reservoir operations in the 10% enhanced scenario (a) and 20% enhanced scenario (b).

Close modal

The discrepancy from the current safety standard indicates that the new drainage threshold as well as more rigorous adaptive measures, such as consolidating river embankment, should be proposed for the future climate. This also agrees with the previous finding that reservoir operations cannot completely eliminate the increasing risks of future floods for this region (Sun et al. 2023). Although climatic factors are rarely considered in practical reservoir operations due to their long-term effects and uncertainty, it is found in this study that neither the conventional nor optimized reservoir operations may guarantee a safe release schedule, because the requirement of the maximum allowed flow at the downstream flood control point becomes outdated.

Targeting the current research gap between the reservoir operations and the inundation risk compounded with climate variations, this work integrated a hydrologic reservoir management model with a 2D hydrodynamic model. The scheduling of the reservoir release was controlled by a conventional regulation model and an optimized model based on the PSO algorithm. Through the comparison, it was found that the optimized operation was always better than the conventional operation in terms of effectively managing the peak discharge at the downstream flood control cross-section and controlling the downstream inundation.

Two reservoir operations optimized by the PSO algorithm were developed with the PSO1 plan focusing on a smaller inundation area and the PSO2 plan focusing on the peak reduction at the flood control point. The comparison indicates that the PSO2 plan was more effective when the single-point peak reduction was the only objective as the common practice, while the PSO1, regarded as the worse choice due to the lower single-point peak reduction, achieved a smaller inundation area that is more favorable for the basin-scale flood resilience. Such conflict indicates the necessity of considering the downstream inundation risk as an additional objective or an evaluation metric during reservoir optimization, which, however, was neglected by most current studies.

This work highlights the need to incorporate 2D downstream inundation risk into reservoir operational optimization frameworks. This imperative becomes particularly urgent, given the projected rise in flood risk due to changing climate patterns. Despite the apparent efficiency of the PSO algorithm in optimizing reservoir operations for the current climate, our analysis proves its inability to address the future climate. Even after the optimization, the downstream area could still expect increased flood exposure due to the increased inundation area and the exceeded safety discharge rate at the flood control cross-section. This indicates that the current maximum allowable flow rate at the flood control point has become outdated and needs to be updated for the future climate.

This work reveals the complex relationship between the reservoir operation and downstream inundation, when dealing with the immense challenges posed by the upcoming climate change. The discrepancy between associating the reservoir operation with and without inundation risk highlights the need to establish the dynamic feedback between the inundation risk and reservoir operations. Jointly addressing this human–natural process could enhance our preparedness for flood risks under future climate conditions.

This work was kindly supported by the Scientific Research Program of The Education Department of Jilin Province (JJKH20231179KJ).

Data cannot be made publicly available; readers should contact the corresponding author for details.

The authors declare there is no conflict.

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